Northumberland County Implementation Plan for the Chesapeake Bay Tributary Strategy A
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Northumberland County Implementation Plan For the Chesapeake Bay Tributary Strategy A. County Description “Chesapeake Bay, the Nation’s largest estuary, has been adversely affected by nutrient enrichment. Excessive nutrients have caused eutrophication, contributing to periods of hypoxia (dissolved-oxygen concentrations lower than 1.0 mg/L) and poor water-clarity conditions that deprive living resources of necessary oxygen and sunlight.”(Sprague et. al. 2000) Freshwater source inputs come from a multitude of different sources, with the Susquehanna River contributing 50% of the freshwater to the Bay. Of the total streamflow into the Bay, the Susquehanna River contributes 60%. Of the total nutrient contribution to the Bay, the Susquehanna River contributes 62% of the total nitrogen and 34% of the total phosphorus. Northumberland County, located at the junction of the North and West Branches of the Susquehanna River, is an area of diverse and unique land uses and cultures. With a total area of 460 square miles and a population of 94,428, Northumberland County is, for the majority, a rural county. With a little over 123,500 acres of farm land within the county limits, agriculture has always been and continues to be a substantial amount of the land use in Northumberland County. The culture of Northumberland County is just as diverse as its land use. The east central and west central parts of the county are mostly urban while the northern half of the county brings in some of the Amish community. Northumberland County contributes approximately 3 million pounds of total nitrogen, 73,000 pounds of total phosphorus and 24,000 tons of total sediment to the Bay each year. Tillage practices, forested areas and urban areas are the largest contributors to this load as can be seen in Appendix #1. As mentioned earlier, agriculture is a large part of the economy and land use of Northumberland County. Ranking fourth in Pennsylvania for the production of corn grain and soybeans and fourteenth in the production of wheat, grain farming is a substantial component of the agriculture in the county. The types and sizes of the livestock operations vary greatly depending on their location within the county. The plan will go into further detail in a later section. 2 B. Water Resources/Quality There are seven major water bodies and their associated watersheds within Northumberland County. Each of these water bodies have their own unique impairments due to the watersheds which impact them. Below is a list of each of these water bodies and their impairments, take note that these are in no order of significance. The charts are in appendix #2. The Mahantango Creek, which forms the southern boundary of the county, has an associated watershed of 28,800 acres. At one time the Mahantango Creek was polluted by abandoned mine discharge. As a result of the efforts of the Mahantango Creek Watershed Association, the Commonwealth of Pennsylvania constructed a mine acid- neutralizing plant in the headwaters of the Mahantango in 1970. Capable of treating up to 32 million gallons of abandoned mine discharge per day, the plant has effectively neutralized acid mine discharge in the Mahantango and has enabled it to support trout and other aquatic life. The population of the watershed is listed at 3,975 people. The land use of the watershed consists mostly of agricultural operations at 15,840 acres (55%), 11,232 acres forested (39%) and 1,728 acres urban (6%). Two major soils associations are predominant in the agricultural areas of this watershed. The Weikert-Berks-Hartleton association is characterized as gently sloping to steep, shallow to deep, well drained soils on hills and ridges; formed in material weathered from shale and some sandstone. The Klinesville-Calvin-Leck Kill association is characterized as gently sloping to steep, shallow to deep, well drained soils on hills and ridges; formed in material weathered from red shale. The major soils associations in Northumberland County are delineated in Appendix #3. The average slope for the watershed is 16.2%. The creek is listed as a warm water fishery and is stocked with trout by the Pennsylvania Fish and Boat Commission. With these types of land use, the major forms of impairments come from non-point source pollution. 3 The Mahantango Creek has been listed on the 303D list due to siltation from removal of vegetation on agricultural operations. One of the main sources of nutrient and sediment loading comes from the livestock feeding areas/barnyards and the untimely and over application of manure to croplands. Also, since the grazed livestock operations in this watershed are mainly beef operations, impacts to stream banks, minimal buffers and overgrazed pastures are a main source of the nutrient and sediment runoff to the watershed’s streams. Another source of non-point source pollution in the watershed comes in the form of conventional tillage and minimal cover crop planting. Due to the steep terrain (8-25% slope) and topography of the watershed, these two impacts produce a substantial amount of nutrient and sediment loading to the Mahantango Creek and its tributaries. The dirt and gravel roads of the Mahantango Creek Watershed are another area of concern. Taking into account the topography and the number of unimproved surfaces in the watershed we can see how these areas can be a major concern of sediment loading to the stream. The Mahantango Creek is part of the Tri-Valley Watershed Association coverage area. The agricultural operations of this watershed consist mainly of grain production and livestock operations. An approximate breakdown by crop for the watershed is as follows; Corn 47.2% 7,476 acres Alfalfa and Hay 12.9% 2,043 acres Set Aside 14.5% 2,297 acres Small Grains 9.9% 1,568 acres Soybeans 9.1% 1,441 acres Pasture 4.7% 744 acres Vegetables and Other 1.7 % 267 acres Total 15,840 acres 4 There are currently 47 livestock operations in the Mahantango Watershed. An approximate breakdown by type of animal is as follows: Type of Operation # of Farms # of Animals Dairy 6 475 Swine 13 16,300 Poultry 8 590,000 Beef 15 1,300 Sheep 5 522 The second major watershed to be discussed is the Mahanoy Creek. With a total watershed area of 100,480 acres, this is one of the larger watersheds in the county. The stream flows east to west through East Cameron, West Cameron and Little Mahanoy townships. The land use for the area is broken down into 66,317 acres forested (66%), 21,101 acres agricultural (21%), 4,019 acres urban (4%) and 9,043 acres mine land (9%). The population of the watershed is listed at 38,824 people. The watershed for this creek includes land in Schuylkill County as well as Columbia County. Two major soils associations are predominant in the agricultural areas of this watershed. The Weikert- Berks-Hartleton association is characterized as gently sloping to steep, shallow to deep, well drained soils on hills and ridges; formed in material weathered from shale and some sandstone. The Klinesville-Calvin-Leck Kill association is characterized as gently sloping to steep, shallow to deep, well drained soils on hills and ridges; formed in material weathered from red shale. The major soils associations in Northumberland County are delineated in Appendix #3. The watershed has an average slope of 19.9%. The Mahanoy Creek is listed as a warm water fishery. Included in the watershed is Schwaben Creek which will be broken into a separate watershed later on. The Mahanoy Creek has a completed TMDL and has been listed on the 303d list as impaired by abandoned mine drainage, siltation from crop related agriculture and atmospheric deposition. The major source of pollution in this watershed is due to abandoned mine drainage from 32 mine discharges with over half of these being considered large discharges (greater than 1.0 cubic foot per second). Agriculture impacts 5 of the watershed are located primarily on the lower reaches of the watershed. One of the main sources of nutrient and sediment loading from agricultural operations comes from the livestock feeding areas/barnyards and the untimely and over application of manure to croplands. Also, since the grazed livestock operations in this watershed are mainly beef and dairy operations, impacts to stream banks, minimal buffers and overgrazed pastures are a main source of the nutrient and sediment runoff to the watershed’s streams. Another source of non-point source pollution in the watershed comes in the form of conventional tillage and minimal cover crop planting. Due to the steep terrain and topography of the watershed, these two impacts produce a substantial amount of nutrient and sediment loading to the Mahanoy Creek and its tributaries. The agricultural operations of this watershed consist mainly of grain production and livestock operations. An approximate breakdown by crop for the watershed is as follows; Corn 49.4% 10,424 acres Small Grains 20.9% 4,410 acres Set Aside 9.7% 2,047 acres Alfalfa and Hay 7.6% 1,604 acres Pasture 7.2% 1,519 acres Soybeans 5.1% 1,076 acres Vegetables and Other 0.1 % 21 acres Total 21,101 acres 6 There are currently 7 livestock operations in the Mahanoy Watershed. An approximate breakdown by type of animal is as follows: Type of Operation # of Farms # of Animals Dairy 2 100 Swine 0 0 Poultry 1 30,000 Beef 4 300 Sheep 1 40 The third watershed to be discussed is the Schwaben Creek watershed. Schwaben Creek is a tributary to the Mahanoy Creek, but due to its drastically different land use, it has been decided to subdivide this stream into a separate watershed.